Biological Control of Desert Locust (Schistocerca Gregaria Forskål)

Total Page:16

File Type:pdf, Size:1020Kb

Biological Control of Desert Locust (Schistocerca Gregaria Forskål) CAB Reviews 2021 16, No. 013 Biological control of desert locust (Schistocerca gregaria Forskål) Eunice W. Githae* and Erick K. Kuria Address: Department of Biological Sciences, Chuka University, P.O. Box 109-60400, Chuka, Kenya. *Correspondence: Eunice W. Githae. Email: [email protected], [email protected] Received: 03 September 2020 Accepted: 05 January 2021 doi: 10.1079/PAVSNNR202116013 The electronic version of this article is the definitive one. It is located here: http://www.cabi.org/cabreviews © CAB International 2021 (Online ISSN 1749-8848) Abstract Desert locust (Schistocerca gregaria Forskål) is one of the most serious agricultural pests in the world due to its voracity, speed of reproduction, and range of flight. We discuss the current state of knowledge on its biological control using microorganisms and botanical extracts. Metarhizium flavoviride was among the first fungus to be recognized as a bio-control agent against desert locust in the laboratory and field conditions. Nevertheless, its oil formulation adversely affected non- target organisms, hence led to further research on other microorganisms. Metarhizium anisopliae var. acridum (syn. Metarhizium acridum) is an environmentally safer bio-pesticide that has no measurable impact on non-target organisms. However, there are various shortcomings associated with its use in desert locust control as highlighted in this review. Bacterial pathogens studied were from species of Bacillus, Pseudomonas, and Serratia. Botanical extracts of 27 plant species were tested against the locust but showed varied results. Azadirachta indica and Melia volkensii were the most studied plant species, both belonging to family Meliaceae, which is known to have biologically active limonoids. Out of the 20 plant families identified, Apiaceae was the most represented with a frequency of 21%. However, only crude botanical extracts were used and therefore, the active ingredients against desert locust were not identified. Through a comprehensive research, an integrated pest management strategy that incorporates these bio-controls would be a realistic option to control desert locust infestations. Keywords: bio-control, bio-pesticides, desert locust, microorganisms, botanical extracts Review Methodology: Research questions were raised using PICO (population, intervention, comparison, and outcomes) and then validated to ensure that they had not been addressed by any other publications. In this case, P-desert locust, I-Bio-control, C-use of chemical pesticides, and O-success of application. A systematic review was then carried out using various keywords. The following search engines and databases were used: Google, Google Scholar, PubMed, ScienceDirect, FAO Desert Locust Information Service, CABI, and HINARI. Titles and abstracts were screened followed by full-text downloading and analysis. Some authors were contacted for full publications where only the abstracts were available. Introduction which is approximately 20% of the earth’s surface [3]. In 1 day, the swarm is capable of consuming the same amount Desert locust (Schistocerca gregaria Forskål) is one of the of food as approximately 35,000 people, with each locust most serious agricultural pests in the world due to its consuming about its own weight of green vegetation [4]. voracity, speed of reproduction, and range of flights, which The plagues are associated with great economic losses can cause huge damage to all plant species [1]. A single hence require urgent attention to safeguard livelihoods swarm can comprise of up to 80 million locusts per square and the environment. kilometer and can fly more than 100 km in the direction of Desert locust invasion is usually restricted to the semi- prevailing winds to cover an area of about 1200 square arid and arid deserts of Africa that receives less than kilometers per day [2]. If left uncontrolled, desert locust 200 mm of rainfall annually [5]. In 1986–1989, desert locust can invade a total area of 28 million square kilometers, plague affected 43 countries after heavy rains. This plague http://www.cabi.org/cabreviews 2 CAB Reviews ended mainly because of control operations and unusual vegetation [16]. If these conditions are unfavorable, the winds that blew swarms across the Atlantic Ocean [6]. swarm migrates until it encounters favorable breeding A similar swarm was witnessed from 2003 to 2005 conditions, which may be thousands of kilometers away where more than 20 countries suffered with an estimated [12]. Effective preventive management strategy should 80–100% loss of crops especially in sub-Saharan Africa [7]. therefore not only rely on the knowledge of the pest During this time, control operations treated nearly biology and ecology but also on the environmental factors 130,000 per square kilometers of the locust infestation associated with its spread. area. The operation took 2 years and spent more than US$ Repeated outbreaks of desert locust in Africa have 400 million to end the plague [6]. Between 2019 and 2020, prompted the use of chemical pesticides as the main exceptional locust breeding was observed in the horn of preventive and control measures. Most of the locust Africa [4]. This magnitude of invasion had not been control measures carried out over the years have used witnessed for more than 70 years in East Africa. A conventional chemical insecticides (organochlorines, prediction model demonstrated that vast areas of Kenya, organophosphates, carbamates, and pyrethroids) that are northeastern regions of Uganda, and some regions of usually neurotoxic to the locust [17]. Although chemical Southern Sudan were at high risk of providing a breeding pesticides may provide an effective means of control due environment for the locust [8]. The onset of long rains to prolonged activity of the spray residue, increased season in East Africa would also remarkably increase the attention has been raised concerning environmental swarms, threatening food security and livelihoods [4]. This damage and human safety [18]. After treatment with rapid and sudden upsurge could be attributed to erratic chemicals, death of insects occurs within hours, making it climatic behavior that is triggered by global warming [9]. difficult to monitor the effects of spray applications However, predictions are mainly based on ecological especially for highly mobile species [19]. As an upsurge aspects but should also integrate the social, economic, and starts, only a few locusts are aggregated into treatable cultural aspects for effective control measures. targets and hence spraying leaves out many individuals that Desert locust is able to change its behavior and continue the upsurge and become aggregated at high physiology in response to environmental conditions, densities [13]. Some chemical insecticides have been transforming the swarms from harmless solitary insects to effective at preventing desert locust outbreaks at very destructive cohesive ones [10]. This feature allows locusts early stages of invasion under Saharan condition but they to survive some of the harshest environmental conditions simultaneously induce heavy mortality in some non-target on earth. Seasonal migration of the desert locust is insect groups [20]. Besides, the outbreaks occur in influenced by various factors such as rainfall, temperature, environmentally sensitive areas especially wetlands, near wind, and vegetation [11]. Favorable conditions for human settlements and to some extent in the protected breeding are moist soils to depths of 10–15 cm, moist bare areas with numerous migratory birds [21]. In East Africa, areas for egg-laying, and green vegetation for hopper current management strategy for desert locust swarms is development [12]. Sparse and erratic seasonal rains aerial spraying with chemical pesticides, which has affected support phase change from their solitary lifestyle to a humans, livestock, and the environment [8]. The concern group lifestyle (gregarious phase) that develop into an regarding use of chemical pesticides provides impetus for upsurge and eventually into a plague [13]. These density- investment in alternative means of control that are dependent changes are adaptations for migration under environmentally friendly and sustainable, such as bio- heterogeneous environmental conditions. For instance, a pesticides [13, 22] even though much remains to be done research study estimated the density of gregarization of in terms of research and implementation. desert locust hoppers in vegetation and reported that Successful control of desert locust will require the vegetation cover and height were the only characteristics development of an integrated pest management program that could enhance prediction of locust phase status [14]. using a variety of products that can be applied with a range A related study reported that low cover and dry vegetation of techniques that are appropriate in different habitats and led to a low density of gregarization while dense and green circumstances [23]. This must be associated with reduced vegetation favored a high density of gregarization, probably pesticide application, economic costs, environmental risks, due to a dispersion rate of the individuals. Another and duration and extent of the locust threat [24]. Proposed experiment explored the influence of vegetation patterns products include bio-pesticides from plants and on gregarization and showed that when the distribution of microorganisms. They are recommended because of their the vegetation was patchy, the locusts were more active,
Recommended publications
  • Locusts in Queensland
    LOCUSTS Locusts in Queensland PEST STATUS REVIEW SERIES – LAND PROTECTION by C.S. Walton L. Hardwick J. Hanson Acknowledgements The authors wish to thank the many people who provided information for this assessment. Clyde McGaw, Kevin Strong and David Hunter, from the Australian Plague Locust Commission, are also thanked for the editorial review of drafts of the document. Cover design: Sonia Jordan Photographic credits: Natural Resources and Mines staff ISBN 0 7345 2453 6 QNRM03033 Published by the Department of Natural Resources and Mines, Qld. February 2003 Information in this document may be copied for personal use or published for educational purposes, provided that any extracts are fully acknowledged. Land Protection Department of Natural Resources and Mines GPO Box 2454, Brisbane Q 4000 #16401 02/03 Contents 1.0 Summary ................................................................................................................... 1 2.0 Taxonomy.................................................................................................................. 2 3.0 History ....................................................................................................................... 3 3.1 Outbreaks across Australia ........................................................................................ 3 3.2 Outbreaks in Queensland........................................................................................... 3 4.0 Current and predicted distribution ........................................................................
    [Show full text]
  • Integration of Entomopathogenic Fungi Into IPM Programs: Studies Involving Weevils (Coleoptera: Curculionoidea) Affecting Horticultural Crops
    insects Review Integration of Entomopathogenic Fungi into IPM Programs: Studies Involving Weevils (Coleoptera: Curculionoidea) Affecting Horticultural Crops Kim Khuy Khun 1,2,* , Bree A. L. Wilson 2, Mark M. Stevens 3,4, Ruth K. Huwer 5 and Gavin J. Ash 2 1 Faculty of Agronomy, Royal University of Agriculture, P.O. Box 2696, Dangkor District, Phnom Penh, Cambodia 2 Centre for Crop Health, Institute for Life Sciences and the Environment, University of Southern Queensland, Toowoomba, Queensland 4350, Australia; [email protected] (B.A.L.W.); [email protected] (G.J.A.) 3 NSW Department of Primary Industries, Yanco Agricultural Institute, Yanco, New South Wales 2703, Australia; [email protected] 4 Graham Centre for Agricultural Innovation (NSW Department of Primary Industries and Charles Sturt University), Wagga Wagga, New South Wales 2650, Australia 5 NSW Department of Primary Industries, Wollongbar Primary Industries Institute, Wollongbar, New South Wales 2477, Australia; [email protected] * Correspondence: [email protected] or [email protected]; Tel.: +61-46-9731208 Received: 7 September 2020; Accepted: 21 September 2020; Published: 25 September 2020 Simple Summary: Horticultural crops are vulnerable to attack by many different weevil species. Fungal entomopathogens provide an attractive alternative to synthetic insecticides for weevil control because they pose a lesser risk to human health and the environment. This review summarises the available data on the performance of these entomopathogens when used against weevils in horticultural crops. We integrate these data with information on weevil biology, grouping species based on how their developmental stages utilise habitats in or on their hostplants, or in the soil.
    [Show full text]
  • Distribution of Methionine Sulfoxide Reductases in Fungi and Conservation of the Free- 2 Methionine-R-Sulfoxide Reductase in Multicellular Eukaryotes
    bioRxiv preprint doi: https://doi.org/10.1101/2021.02.26.433065; this version posted February 27, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 1 Distribution of methionine sulfoxide reductases in fungi and conservation of the free- 2 methionine-R-sulfoxide reductase in multicellular eukaryotes 3 4 Hayat Hage1, Marie-Noëlle Rosso1, Lionel Tarrago1,* 5 6 From: 1Biodiversité et Biotechnologie Fongiques, UMR1163, INRAE, Aix Marseille Université, 7 Marseille, France. 8 *Correspondence: Lionel Tarrago ([email protected]) 9 10 Running title: Methionine sulfoxide reductases in fungi 11 12 Keywords: fungi, genome, horizontal gene transfer, methionine sulfoxide, methionine sulfoxide 13 reductase, protein oxidation, thiol oxidoreductase. 14 15 Highlights: 16 • Free and protein-bound methionine can be oxidized into methionine sulfoxide (MetO). 17 • Methionine sulfoxide reductases (Msr) reduce MetO in most organisms. 18 • Sequence characterization and phylogenomics revealed strong conservation of Msr in fungi. 19 • fRMsr is widely conserved in unicellular and multicellular fungi. 20 • Some msr genes were acquired from bacteria via horizontal gene transfers. 21 1 bioRxiv preprint doi: https://doi.org/10.1101/2021.02.26.433065; this version posted February 27, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license.
    [Show full text]
  • Potential Impact of Desert Locust to Nutrition Security in SOMALIA
    POTENTIAL IMPACT OF DESERT LOCUST Emma Apo Ouma TO NUTRITION SECURITY IN SOMALIA WHAT IS THE CURRENT SITUATION? •Triple threat of Desert Locust, Gu flooding and COVID-19, •April and June 2020, an estimated 2.7 million people across Somalia are expected to face Crisis and deteriorate to 3.5 million between July and September 2020 WHAT DOES THIS MEAN FOR NUTRITION SECURITY? CROP AND PASTURE DAMAGE Threat to current Gu season crop production and may also threaten pasture availability and crop cultivation across Somalia through the following 2020 Deyr (October-December A swarm can eat enough food in one day to feed 34 million people. FALLING LIVESTOCK PRICES •Livestock diseases •Poor livestock nutrition; increased price of livestock feed •Reduced quality of livestock products eg milk, meat LOSS OF LIVELIHOODS •Disruption of food systems; critical value chains have been affected e.g. livestock, cereals such as sorghum, maize •Loss of wage and employment opportunities e.g. labor in the fields, value chain actors •Increase in livelihood based coping strategy: eg selling last breeding animal, spent savings, begging, reduced expenditure on livestock and agriculture •Reduced spending on non-food needs health care, education FOOD CONSUMPTION AND DIETARY DIVERSITY •With poor harvests, there is likelihood of poor food consumption at hhd level •Depletion of food stocks •Food Prices have increased •A majority if households rely on markets for food: increased reliance on purchased and processed foods •Compromise the nutrition of the most vulnerable: children less than 5, PLW, elderly, adolesents •Increased rates of acute malnutrition ONGOING EFFORTS Household Level Screening and referral of acute malnutrition cases Targeting of the most vulnerable (UCT) Community level ▪Burying locusts, setting fires, and making noise to scare them off.
    [Show full text]
  • Guidance for POP Pesticides
    Guidance for POP pesticides 1. Background on POP pesticides POPs Pesticides originate almost entirely from anthropogenic sources and are associated largely with the manufacture, use and disposition of certain organic chemicals. Of the initial 12 POPs chemicals, eight are POPs pesticide. In the new POP list, five chemicals may be categorised as pesticides. These are alpha hexachlorocyclohexane (alpha-HCH), beta hexachlorocyclohexane (beta-HCH), Chlordecone, Lindane (gamma, 1,2,3,4,5,6- hexaclorocyclohexane) and Pentachlorobenzene. This module addresses baseline data gathering and assessment of POPs pesticides. Particular care is required to address DDT due to its use for vector control and Lindane due to its use for control of ecto-parasites in veterinary and human application, which may be under the responsibility of authorities other than those responsible for primarily agricultural chemicals. In addition, it is important that all uses of HCB, alpha hexachorocyclohexane, beta hexachlorocyclohexane and pentachlorobenzene (industrial as well as pesticide) be properly addressed. Specialists with knowledge of each of these areas might be included in the task teams. 2. Objective To review and summarize the production, use, import and export of the chemicals listed in Annex A and Annex B of the Convention (excluding other chemicals listed under Annex A and B which are not considered as pesticides). To gather information on stockpiles and wastes containing, or thought to contain, POPs pesticides. To assess the legal and institutional framework for control of the production, use, import, export and disposal of the chemicals listed in Annex A and Annex B (excluding other chemicals which are not classed as pesticides) of the Convention.
    [Show full text]
  • Periodical Cicadas SP 341 3/21 21-0190 Programs in Agriculture and Natural Resources, 4-H Youth Development, Family and Consumer Sciences, and Resource Development
    SP 341 Periodical Cicadas Frank A. Hale, Professor Originally developed by Harry Williams, former Professor Emeritus and Jaime Yanes Jr., former Assistant Professor Department of Entomology and Plant Pathology The periodical cicada, Magicicada species, has the broods have been described by scientists and are longest developmental period of any insect in North designated by Roman numerals. There are three 13-year America. There is probably no insect that attracts as cicada broods (XIX, XXII and XXIII) and 12 17-year much attention in eastern North America as does the cicada broods (I-X, XIII, and XIV). Also, there are three periodical cicada. Their sudden springtime emergence, distinct species of 17-year cicadas (M. septendecim, filling the air with their high-pitched, shrill-sounding M. cassini, and M. septendecula) and three species of songs, excites much curiosity. 13-year cicadas (M. tredecim, M. tredecassini, and M. tredecula). Two races of the periodical cicada exist. One race has a life cycle of 13 years and is common in the southeastern In Tennessee, Brood XIX of the 13-year cicada had a United States. The other race has a life cycle of 17 years spectacular emergence in 2011 (Map 1). In 2004 and and is generally more northern in distribution. Due 2021, Brood X of the 17-year cicada primarily emerged to Tennessee’s location, both the 13-year and 17-year in East Tennessee (Map 2). Brood X has the largest cicadas occur in the state. emergence of individuals for the 17-year cicada in the United States. Brood XXIII of the 13-year cicada last Although periodical cicadas have a 13- or 17-year cycle, emerged in West Tennessee in 2015 (Map 3).
    [Show full text]
  • The Transcriptomic and Genomic Architecture of Acrididae Grasshoppers
    The Transcriptomic and Genomic Architecture of Acrididae Grasshoppers Dissertation To Fulfil the Requirements for the Degree of “Doctor of Philosophy” (PhD) Submitted to the Council of the Faculty of Biological Sciences of the Friedrich Schiller University Jena by Bachelor of Science, Master of Science, Abhijeet Shah born on 7th November 1984, Hyderabad, India 1 Academic reviewers: 1. Prof. Holger Schielzeth, Friedrich Schiller University Jena 2. Prof. Manja Marz, Friedrich Schiller University Jena 3. Prof. Rolf Beutel, Friedrich Schiller University Jena 4. Prof. Frieder Mayer, Museum für Naturkunde Leibniz-Institut für Evolutions- und Biodiversitätsforschung, Berlin 5. Prof. Steve Hoffmann, Leibniz Institute on Aging – Fritz Lipmann Institute, Jena 6. Prof. Aletta Bonn, Friedrich Schiller University Jena Date of oral defense: 24.02.2020 2 Table of Contents Abstract ........................................................................................................................... 5 Zusammenfassung............................................................................................................ 7 Introduction ..................................................................................................................... 9 Genetic polymorphism ............................................................................................................. 9 Lewontin’s paradox ....................................................................................................................................... 9 The evolution
    [Show full text]
  • The Cytology of Tasmanian Short-Horned Grasshoppers ( Orthoptera: Acridoidea)
    PAP. & PROC. ROY. Soc. TASMANIA. VOL. 86. (15TH SEPTEMBER. 1952.) The Cytology of Tasmanian Short-Horned Grasshoppers ( Orthoptera: Acridoidea) By G. B. SHARMAN Department of Botany, University of Tasmania* WITH 1 PLATE AND 57 TEXT FIGURES SUMMARY The cytology of twenty-six of the twenty-nine species of short-horned grass­ hoppers (superfamily Acridoidea) recorded from Tasmania is described. Intra­ specific cytological polymorphism is described in some species. Cytological evidence of phylogenetic relationships has been indicated where possible. INTRODUCTION Mainly because of their large size, and general suitability for cyto­ logical study the chromosomes of the short-horned grasshoppers (super­ family Acridoidea) have been the subject of wide research. In the largest and most widely studied family, the Acrididae, early workers (McClung, 1905; Davis, 1908) reported the male number as being uniformly twenty­ three rod-shaped chromosomes, but Granata (1910) showed that Pam­ phagus possessed nineteen rod-shaped chromosomes. With few exceptions an XO sex chromosome sy~tem is found. Later work has shown that one group of subfamilies of the Acrididae is characterised by the male diploid number of· nineteen rod-shaped chromosomes, whilst another and larger group is characterised by the male diploid number of twenty-three. These are usually called the ten and twelve chromosome groups, and correspond to the Chasmosacci and Cryptosacci groups of subfamilies (Roberts, 1941). Cytologically the Chasmosacci is a very uniform group as has been shown by Rao (1937) and Powers (1942). The twelve chromosome group, how­ ever, has some cytological variability. In more than forty genera the characteristic male diploid chromosome number of twenty-three is found (White, 1945) ; but" centric fusions" (White, 1945) have been responsible for lowering the chromosome number of some species, although the characteristic twenty-three arms are still found.
    [Show full text]
  • Desert Locusts in Eastern Africa
    FACTS & FIGURES 9 countries affected in Greater Horn of Africa: Ethiopia, Somalia, Sudan, and Kenya worst affected 30.5 million people already severely food insecure in the region EU humanitarian funding: • €66 million allocated by the EU for Desert Locust related response (€41 million from EU humanitarian aid, €25 million from EU development aid) in 2020 • €8 million to support desert locusts’ surveillance and control operations in Ethiopia, Somalia, Kenya and Sudan in 2021 ©FAO/Sven Torfinn Last updated 28/06/2021 European Civil Protection and Humanitarian Aid Operations Desert locusts in Eastern Africa Introduction Since 2019, Eastern Africa has seen an upsurge of desert locusts, spreading across several countries at rates not seen in decades. At the end of 2020, the situation was still critical in the whole region. Thanks to major control efforts, the pest seems almost eradicated in Kenya and Sudan in 2021. However, populations of desert locust have been identified breeding in several areas in eastern Ethiopia and northern Somalia. This is due to the favourable conditions created by the short rainy season at the end of 2020 and early this year. New generations of hoppers are expected to move by the end of June 2021 towards north-eastern Somalia and northern areas of Ethiopia, threatening the harvest season and pasture areas. It is also necessary to monitor swarms that could come from Yemen, where the Desert Locust population remains high. With over 30 million people already severely food insecure in the region, the locust upsurge is an additional threat to food security. What are the needs? The food security situation could deteriorate further due to the impact of the multiple threats the region faces: (i) conflict, (ii) desert locusts, (iii) natural hazards caused by climate change (floods and droughts), (iv) economic crisis, and (v) the effects of the ongoing coronavirus pandemic.
    [Show full text]
  • An Illustrated Key of Pyrgomorphidae (Orthoptera: Caelifera) of the Indian Subcontinent Region
    Zootaxa 4895 (3): 381–397 ISSN 1175-5326 (print edition) https://www.mapress.com/j/zt/ Article ZOOTAXA Copyright © 2020 Magnolia Press ISSN 1175-5334 (online edition) https://doi.org/10.11646/zootaxa.4895.3.4 http://zoobank.org/urn:lsid:zoobank.org:pub:EDD13FF7-E045-4D13-A865-55682DC13C61 An Illustrated Key of Pyrgomorphidae (Orthoptera: Caelifera) of the Indian Subcontinent Region SUNDUS ZAHID1,2,5, RICARDO MARIÑO-PÉREZ2,4, SARDAR AZHAR AMEHMOOD1,6, KUSHI MUHAMMAD3 & HOJUN SONG2* 1Department of Zoology, Hazara University, Mansehra, Pakistan 2Department of Entomology, Texas A&M University, College Station, TX, USA 3Department of Genetics, Hazara University, Mansehra, Pakistan �[email protected]; https://orcid.org/0000-0003-4425-4742 4Department of Ecology & Evolutionary Biology, University of Michigan, Ann Arbor, MI, USA �[email protected]; https://orcid.org/0000-0002-0566-1372 5 �[email protected]; https://orcid.org/0000-0001-8986-3459 6 �[email protected]; https://orcid.org/0000-0003-4121-9271 *Corresponding author. �[email protected]; https://orcid.org/0000-0001-6115-0473 Abstract The Indian subcontinent is known to harbor a high level of insect biodiversity and endemism, but the grasshopper fauna in this region is poorly understood, in part due to the lack of appropriate taxonomic resources. Based on detailed examinations of museum specimens and high-resolution digital images, we have produced an illustrated key to 21 Pyrgomorphidae genera known from the Indian subcontinent. This new identification key will become a useful tool for increasing our knowledge on the taxonomy of grasshoppers in this important biogeographic region. Key words: dichotomous key, gaudy grasshoppers, taxonomy Introduction The Indian subcontinent is known to harbor a high level of insect biodiversity and endemism (Ghosh 1996), but is also one of the most poorly studied regions in terms of biodiversity discovery (Song 2010).
    [Show full text]
  • Desert Locust Threat in the Sahel and West Africa
    Desert Locust threat in the Sahel and West Africa Resilience Working Group Meeting (11 September 2020) Outline of Presentation 1. Original Risk of Desert Locust invasion 2. Potential impacts on food security 3. FAO’s Response Plan 4. Current Desert Locust situation and forecast 5. Ongoing activities ‐ Level of response 6. Resource mobilization Commission de Lutte contre le Criquet Pèlerin Resilience Team West Africa/Sahel dans la Région Occidentale (CLCPRO) 2 1. Original Risk of Desert Locust invasion in West Africa and the Sahel March 2020 : FAO/CLCPRO suggests that swarms may arrive in the Sahel from the Horn of Africa May 2020 : FAO Desert Locust Information Service (DLIS) confirms the risk of swarms appearing in the Sahel (Eastern Chad) from breeding areas in Saudi Arabia and Eastern Africa (Kenya, Ethiopia) as early as June 2020 May, 21st 2020 : FAO’s Regional Desert locust crisis Appeal for West Africa (May‐December 2020) launched CLCPRO : Commission for controlling the DL in Western Region Commission de Lutte contre le Criquet Pèlerin Resilience Team West Africa/Sahel dans la Région Occidentale (CLCPRO) 2. Impacts potentiels sur la sécurité alimentaire2. Potential impacts on food security Desert Locust = the world's oldest migratory pest and dangerous predator 1 swarm of 1 km2 can consume as much food as 35,000 people in one day Serious threat to food security and people's livelihoods With a locust invasion : 9.3 million people in crisis and worse In addition to the 17 million already projected for the lean season (June‐Aug. 2020) ‐ CH Econometric model: Estimated impact of locust attack on agricultural production (millet, sorghum and groundnut crops) and pasture/fodder.
    [Show full text]
  • Grasshoppers
    Grasshoppers Orthoptera: Acrididae Plains Lubber Pictured grasshoppers Great crested grasshopper Snakeweed grasshoppers Primary Pest Grasshoppers • Migratory grasshopper • Twostriped grasshopper • Differential grasshopper • Redlegged grasshopper • Clearwinged grasshopper Twostriped Grasshopper, Melanoplus bivittatus Redlegged Grasshopper, Melanoplus femurrubrum Differential Grasshopper, Melanoplus differentialis Migratory Grasshopper, Melanoplus sanguinipes Clearwinged Grasshopper Camnula pellucida Diagram courtesy of Alexandre Latchininsky, University of Wyoming Photograph courtesy of Jean-Francoise Duranton, CIRAD Grasshoppers lay pods of eggs below ground Grasshopper Egg Pods Molting is not for wimps! Grasshopper Nymphs Some grasshoppers found in winter and early spring Velvet-striped grasshopper – a common spring species Grasshopper Controls • Weather (rainfall mediated primarily) • Natural enemies – Predators, diseases • Treatment of breeding areas • Biological controls • Row covers Temperature and rainfall are important mortality factors Grasshoppers and Rainfall Moisture prior to egg hatch generally aids survival – Newly hatched young need succulent foliage Moisture after egg hatch generally reduces problems – Assists spread of diseases – Allows for plenty of food, reducing competition for rangeland and crops Grasshopper predators Robber Flies Larvae of many blister beetles develop on grasshopper egg pods Blister beetle larva Fungus-killed Grasshoppers Pathogen: Entomophthora grylli Mermis nigrescens, a nematode parasite of grasshoppers
    [Show full text]